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A Critical Conversation on Climate Change ... - Green Choices

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offsets – the fossil ec<strong>on</strong>omy’s new arena of c<strong>on</strong>flict 253A new teak plantati<strong>on</strong>near the San Carlos Riverin northern Costa Rica.Exposed soil heated bydirect tropical sunlight islikely to release significantquantities of carb<strong>on</strong>.A Costa Rican acaciaplantati<strong>on</strong>. The logs in theforeground have beendiscarded and left to rot.In a few years, they willrelease all their carb<strong>on</strong>back to the atmosphere.say, 100 years, it does not necessarily follow that carb<strong>on</strong> sequesteredfor 10 years will have <strong>on</strong>e-tenth the climatic effect of carb<strong>on</strong> sequesteredfor 100 years. Again, the problem is not that any given patchof trees is temporary, but that there’s so much uncertainty and ignoranceabout how to measure its relevance to climate. It’s not a matterof calculable ‘risk’, but something far more recalcitrant to marketaccounting.In additi<strong>on</strong>, t<strong>on</strong>ne-year accounting can make what allowances it doesmake for uncertainty <strong>on</strong>ly at the cost of generating carb<strong>on</strong> creditsslowly. That makes it unattractive to business. It also militates againstsmall projects. The CATIE study found that at prices of usd 18 pert<strong>on</strong>ne – more than actual prices as of 2006 – the t<strong>on</strong>ne-year methodologywould allow profits <strong>on</strong>ly in projects of over 40,000 hectares.Then there is a method called ‘average storage adjusted for equivalencetime’ (ASC), which generates credits more quickly.Other methods include the UN’s ‘temporary’ Certified Emissi<strong>on</strong>sReducti<strong>on</strong>s (tCERs), which expire at the end of the Kyoto Protocol’ssec<strong>on</strong>d commitment period and must be replaced if retired forcompliance in the first commitment period; and ‘l<strong>on</strong>g-term’ credits(lCER)s, which expire and must be replaced if the afforestati<strong>on</strong> orreforestati<strong>on</strong> project is reversed or fails to be verified. N<strong>on</strong>e of theseapproaches, however, address the basic problems of uncertainty andignorance described in Chapter 3. In fact, not even the atmosphericlifetime of carb<strong>on</strong> dioxide emissi<strong>on</strong>s can be pinned down with anyprecisi<strong>on</strong>, as menti<strong>on</strong>ed above. For business, this translates into accountingheadaches and high ec<strong>on</strong>omic risk.In the end, CATIE came to the c<strong>on</strong>clusi<strong>on</strong> that CDM forestryprojects had to be big in order for it to be worthwhile to fulfil all theaccounting and other requirements. Out of a total of over 1,500 simulatedscenarios, <strong>on</strong>ly 8 per cent made it possible for projects under500 hectares to participate. The mean size of a profitable project was5,000 hectares. One way out would be to bundle smaller projectstogether and employ standardised assumpti<strong>on</strong>s and procedures, butagain that would magnify accounting mistakes and also would behard to achieve, given the Costa Rican land tenure system.You’ve talked a lot about how much harder it is to measure how much carb<strong>on</strong> issequestered in tree projects than simply to keep fossil carb<strong>on</strong> in the ground. Butmaybe we d<strong>on</strong>’t need to compare carb<strong>on</strong> sequestered in trees with carb<strong>on</strong> storedin fossil deposits. We should think of forestry carb<strong>on</strong> projects like Costa Rica’sas replacing carb<strong>on</strong> released from forests, not as replacing carb<strong>on</strong> released fromfossil fuel combusti<strong>on</strong>. This should solve the measurement problem, since all wehave to do is compare biotic carb<strong>on</strong> with other biotic carb<strong>on</strong>.

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